X-ray and ultraviolet photoelectron spectroscopy (XPS and UPS, respectively) and scanning tunneling microscopy (STM) were used to observe the initial oxidation of pyrite surfaces in air. The results show the growth of oxide-like oxidation products, with minor contributions from sulfate. UPS shows a decrease in the density of electronic states in the uppermost valence band of pyrite, corresponding to oxidation of surface Fe2+. This allows reliable interpretation of STM images, which show that initial surface oxidation of FeH proceeds by growth of oxidized patches. The borders of oxidized patches contain small segments oriented in the (110) and (100) directions. STM of as-received pyrite cube surfaces, oxidized in air for years, also show the importance of the (110) crystallographic directions, on the surface, in controlling reaction progress. A model in which oxidation probabilities for FeH surface sites are proportional to the number of nearest-neighbor oxidized (FeH) sites was tested using a Monte Carlo approach and reproduces the surface patterns observed in STM. An oxidation mechanism consistent with the XPS, UPS, STM, and Monte Carlo results is proposed. The rate constant for electron transfer from surface-exposed pyrite FeH to O2 is small. Electron transfer is more rapid from pyrite FeH to FeH present on the surface as an oxidation product, such as in the patches we observed. FeH in oxide is a better reductant than FeH in pyrite, so electron transfer to O2 from the oxide is also fast. However, this two-step mechanism is faster overall only if electron transfer to the surface oxide patches is irreversible (e.g., because ofS2 oxidation or electron hopping within the surface oxide patches). Cycling of Fe between the FeH and FeH forms, particularly along borders between oxidized and unoxidized areas, is thus a key feature of the pyrite oxidation mechanism. An understanding of the surface electronic and band structure aids definition of the redox potentials of electrons in various surface states. Rates of electron transfer from these states to O2 are estimated using a kinetic theory of elementary heterogeneous electron transfer. 1994), reduction of aqueous trace metal complexes to form ore deposits (Jean and Bancroft 1985; Bakken et al. 1989), and nutrient and metal cycling at oxic-anoxic boundaries on lake bottoms and in estuaries (Morse 1994). Pyrite oxidation is also important in technological applications ranging from hydrometallurgy (Buckley and Woods 1987; Karthe et al. 1993) to solar energy conversion (Ennaoui et al. 1986). Geochemical understanding of pyrite oxidation is largely based on wet-chemical studies of overall rates and stoichiometries. Important oxidants (e.g., O2 and FeH) have been identified and widely applicable rate laws developed (e.g., Singer and Stumm 1970; Williamson and Rimstidt 1994). Reaction mechanisms are less well * Present address: Department of Geology and Geophysics, known. Predicting and controlling the environmental asUniversity of Wyoming, Laramie, Wyoming 82071-3006, U.S.A. pects of pyrite oxidation, such as the role ofFeH at pyrite 0003-004X/96/091 0-1 036$05.0